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EC number: 228-771-0 | CAS number: 6358-37-8
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- From 26 APR 1994 to 06 JUN 1994
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Guideline study (OECD TG 474)
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 994
- Report date:
- 1994
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- yes
- Remarks:
- only 1000 instead of 2000 immature erythrocytes were evaluated per animal
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.12 (Mutagenicity - In Vivo Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- yes
- Remarks:
- only 1000 instead of 2000 immature erythrocytes were evaluated per animal
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- in accordance with Directive 88/320/EEC
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- 2,2'-[(3,3'-dichloro[1,1'-biphenyl]-4,4'-diyl)bis(azo)]bis[N-(4-methoxyphenyl)-3-oxobutyramide]
- EC Number:
- 250-797-6
- EC Name:
- 2,2'-[(3,3'-dichloro[1,1'-biphenyl]-4,4'-diyl)bis(azo)]bis[N-(4-methoxyphenyl)-3-oxobutyramide]
- Cas Number:
- 31775-16-3
- IUPAC Name:
- 2,2'-[(3,3'-dichlorobiphenyl-4,4'-diyl)didiazene-2,1-diyl]bis[N-(4-methoxyphenyl)-3-oxobutanamide]
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- ICR
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Harlan U.K. Ltd., blackthorn, Bicester, Oxon, U.K.
- Age at study initiation: 5-8 weeks
- Weight at study initiation: males: 21-30 g; females: 20-25 g
- Assigned to test groups randomly: yes
- Housing: in groups up to five by sex
- Diet: Rat and Mouse Expanded Diet No. 1 (Special Diet Services Ltd. Witham, Essex, U.K.), ad libitum
- Water: tap water, ad libitum
- Acclimation period: at least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20-22
- Humidity (%): 44-50
- Air changes (per hr): 15
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- - Vehicle used: arachis oil
- Concentration of test material in vehicle: 125, 250 or 500 mg/ml
- dose volume: 10 ml/kg
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
- test material was freshly prepared as a suspension at the appropriate concentration in arachis oil
- analysis of concentration, homogeneity and stability was not performed
APPLICATION:
- single intraperitoneal application - Duration of treatment / exposure:
- 1250 and 2500 mg/kg group: 24 hrs
5000 mg/kg group: 24, 48 and 72 hrs - Frequency of treatment:
- single
- Post exposure period:
- none
Doses / concentrations
- Remarks:
- Doses / Concentrations:
1250, 2500, 5000 mg/kg bw
Basis:
nominal conc.
- No. of animals per sex per dose:
- 5 males and 5 females per dose and exposure duration
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- - cyclophosphamide
- Route of administration: intraperitoneal
- Doses / concentrations: 50 mg/kg
- Exposure duration: 24 hrs
Examinations
- Tissues and cell types examined:
- bone marrow cells from the femur
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION:
- maximum recommended dose level and two lower dose levels
DETAILS OF SLIDE PREPARATION:
- femur was dissected from each animal, aspirated with foetal calf serum and bone marrow smears were prepared following centrifugation and re-suspension. Smears were air-dried, fixed in absolute methanol and stained with May-Grünwald/Giemsa
METHOD OF ANALYSIS:
- blind examination with light microscopy
- scoring of micronucleated cells per 1000 polychromatic erythrocytes per animal
- normochromatic erythrocytes associated with 1000 erythrocytes were counted ans scored for incidence of micronuclei
- calculation of polychromatic to normochromatic erythrocytes
- Evaluation criteria:
- - a statistically significant increase in the number of micronucleated polychromatic erythrocytes in the treatment groups in comparison to the control group is evaluated as positive mutagenic response
- a positive response for bone marrow toxicity is demonstrated when the dose group mean polychromatic to normochromatic ratio is shown to be statistically significant from the concurrent vehicle control group - Statistics:
- - Student's t-test
- one way analysis of variance
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
- Dose range: 500-5000 mg/kg bw, i.p; 500-2000 mg/kg bw, oral
- Clinical signs of toxicity in test animals: hunched posture and fur stained orange; one premature death at 2000 mg/kg bw i.p., which was considered to be due to poor dosing technique rather than to toxicity of the test material
RESULTS OF DEFINITIVE STUDY
- Ratio of PCE/NCE (for Micronucleus assay): group means for control groups: 1.46 - 1.83; treatment groups did not deviate significantly
Any other information on results incl. tables
- no premature deaths in any dose group
- fur stained with test material in all animals treated with the test item
- hunched posture in some animals at 5000 mg/kg bw
- one animal with lethargy at 5000 mg/kg bw
There was no statistically significant increase in the frequency of micronucleated PCE's and in the PCE/NCE ratio in any dose group when compared to the concurrent vehicle control groups.
The positive control goup showed a marked increase in the incidence of micronucleated PCE.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
The test item was considered to be non-genotoxic under the conditions of this in vivo micronuclei assay. - Executive summary:
Genetic toxicity of the test item has been investigated in an in vivo micronucleus assay in male and female ICR mice (5 per sex and group). The test item was administered at the maximum recommended dose level of 5000 mg/kg bw, with 2500 and 1250 mg/kg bw as the two lower dose levels. Animals were killed 24, 48 or 72 hours later. Evaluation of polychromatic (PCE) or normochromatic (NCE) erythrocytes did not reveal any evidence of an increase in the incidence of micronucleated cells. No significant change in the PCE/NCE ratio was observed after dosing with the test item, however, clinical signs were observed in animals dosed with the test item and as such are evidence of systemic exposure. The positive control material produced a marked increase in the frequency of micronucleated PCE. The test material was considered to be non-genotoxic under the conditions of the test.
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